High Resolution Quantitation of Microcystins with SCIEX X500R QTOF System KC Hyland
Microcystins and Environmental Analysis Why microcystins and nodularins? Toxic products of cyanobacteria and aquatic microfauna Microcystins represent an important contaminant class for environmental and drinking water analysis US EPA UCMR4 list, effective starting in 2018 LC-MS/MS Analysis Commonly conducted on triple quadrupole systems for sensitivity and robustness Environmental testing labs are frequently confronted with the need for more confirmatory information Positive analyte identification in real world samples False positives impact water supply Increased interest and adoption of high resolution/accurate mass (HRAM) systems Specificity and qualitative confirmation of compound identification, while maintaining sensitive, robust, routine quantitation
Overview Key Points Demonstrated Methods and data are presented which demonstrate use of HRAM for accurate and sensitive quantitation of microcystins and nodularin in water samples. Quantitation of a suite of eight microcystins (MC) and one nodularin (NOD) was achieved using high resolution accurate mass LC-MS/MS with the SCIEX X500R QTOF system.
SCIEX X500R QTOF System Engineered for simplicity, functionality Shorter vertical profile and improved thermal insulation with “N” TOF flight path. Minimized footprint The benchtop stature (110 x 57 x 112 cm)* occupies less lab space than any other HRMS system on the market. TwinSpray An independent calibrant delivery path for auto-calibration that doesn’t interfere with heating within the source. Turbo V Source Proven ruggedness with capability for ESI and APCI configurations. Integrated calibration Maintains mass calibration through long runs without effect on sample flow. Completely integrated design eliminates external pumping systems.
SCIEX OS Software – Home Processing Simultaneous Identification and quantitation Acquisition Build MS and LC methods Create batches Run samples Management Adjust hardware, software, and user settings
Analytical Conditions HPLC Conditions TOF MS Conditions SCIEX ExionLC™ AD Chromatographic separation under gradient conditions using a Phenomenex Kinetex® C8 column (2.6 μm particle size, 100 x 3 mm) Flow rate of 0.500 mL/min. Column oven temperature was 40°C and a 20 μL injection Run time was 11 minutes for the full gradient SCIEX X500R QTOF system Turbo V™ source operated in positive mode electrospray ionization (ESI) TOF MS scan conducted from 500-1100 m/z MRMHR experiment monitored 2 transitions for each analyte Optimized compound-specific voltages were designated for maximum sensitivity and specificity RT values were specified for each MRMHR transition to optimize cycle time for best peak shape and quantitation
Notes on Chromatography The 11-minute chromatographic gradient with the Kinetex C8 column achieved baseline separation for all compounds. The gradient is 15 min shorter than the program described in EPA Method 544, resulting in considerable time savings while maintaining separation and peak quality
Data Processing- Extracting Target Masses from TOFMS Data Quantitation was achieved by utilizing high resolution TOF MS data of each precursor. MRMHR transitions were acquired and used for quantitation and confirmation. Both scans occur within every cycle during an injection, and processing of the acquired data can utilize either or both. TOF MS data was processed using known analyte charged monoisotopic masses (m/z) and a mass extraction width (XIC width) of 0.02 Da Accurate Masses for Microcystins and Nodularin. The formula and accurate monoisotopic m/z for each analyte studied is provided. Compound ID Formula Adduct Monoisotopic m/z MC-RR C49H75N13O12 [M+2H]++ 519.79018 Nodularin C41H60N8O10 [M+H]+ 825.45052 MC-LA C47H68N6O12 909.49680 MC-LF C52H71N7O12 986.52335 MC-LR C49H74N10O12 995.55604 MC-LY C52H71N7O13 1002.51826 MC-LW C54H72N8O12 1025.53425 MC-YR C52H72N10O13 1045.53531 MC-WR C54H73N11O12 1068.55129 Building a processing method for quantitation based on TOFMS data is as simple as entering the formula and expected adduct. The software calculates the monoisotopic mass and pulls the extracted peak from the TOF MS trace.
Data Analysis and Method Performance Evaluation Data acquisition and processing were performed using SCIEX OS software. Calibration curves over seven concentration levels from 0.12-312 µg/L Linear regression models with 1/x weighting to fit all calibration curves (LOD) was defined as the lowest calibrator S/N ≥3 and (LOQ) was defined as the lowest calibrator with S/N ≥10
Data Analysis and Method Performance Evaluation Using the TOF MS for quantitation results in excellent sensitivity with sub-ppb detection limits and exceptional precision at low and mid range concentrations
High Quality MS and MSMS Data for Confirmation A key advantage of HRAM approach to quantitation is the ability to apply multiple points of confirmation to avoid reporting false positive detection The five points of confirmation applied in this method are: Accurate mass of the target precursor Confirmation with the MRMHR transition and the accurate mass of the fragment ion Isotope ratio matching to theoretical pattern based on target formula Ion ratio matching between standard and unknown sample Retention time matching between standard and sample
Mass Accuracy Match: TOF MS
Mass Accuracy Match: TOF MS/MS
Qualitative Tools for Matching can be used Simultaneously Mass accuracy within 2ppm reinforces confidence in the identification of the targets High resolution fragments collected using MRMHR also demonstrate excellent specificity and confidence TOF MS pattern of resolved MS isotopes compared to the theoretical isotope pattern provide additional confirmation and are displayed in the results Precursor XIC and MRMHR transition data grouped together allows the software to automatically evaluate ion ratios as another metric for matching and confirmation
Summary Quantitation of a suite of microcystins and nodularin was demonstrated using LC-MS/MS on SCIEX X500R QTOF system. Excellent quantitation results with sensitive detection (<0.1μg/L LOD) and exceptional reproducibility (%CV <7%) at low concentrations If used with the EPA Method 544 suggested concentration factor of 500-fold, these detection limits are theoretically extended to 0.0002 μg/L Concurrent MRMHR data allows for additional quantitative information and enhanced confidence in qualitative analysis without requiring additional injections or processing. HRAM approach provides confirmation of target identification using accurate precursor mass matching, isotope pattern matching, accurate fragment mass matching, ion ratio matching, and retention time matching Verifying across these five points reinforces the ability to confirm the presence of the analyte and helps safeguard against reporting false positives
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